Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Old Mans Creek IA 02-IOW-686

from confluence with unnamed tributary (N line S1 T78N R7W Johnson Co.) to confluence with unnamed tributary in NE 1/4 S4 T78N R8W Johnson Co.

Assessment Cycle
2018
Release Status
Final
Data Collection Period
Overall IR Category
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
5/14/2019 6:52:14 AM
Updated
7/18/2019 2:56:43 PM
Assessment conducted in accordance with Iowa's 2018 IR methodology
Use Support
Class A1
Not Supported
Bacteria: Indicator Bacteria- E. coli
Support Level
Not Supported
Impairment Code
5p - Impairment occurs on a waterbody with a presumptive A1 or B(WW1) use.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2008
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Ambient monitoring: Iowa DNR-rivers
TMDL Priority
Tier III
Class BWW2
Partially Supported
Biological: low fish IBI
Support Level
Partially Supported
Impairment Code
5b-t - Biological - tentative
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2006
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
TMDL Priority
Tier IV
General Use
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The presumptive Class A1 (primary contact recreation) uses remain assessed (monitored) as "not supported" due to levels of indicator bacteria that violate state water quality criteria.  The Class B(WW2) aquatic life uses are assessed (evaluated) as "partially supported” based on results of biological sampling in 2010, 2015 and 2016.  Sources of data used for this assessment include (1) results of DNR/SHL monthly ambient water quality monitoring conducted on Old Mans Creek near Iowa City at the County Road W62 bridge (STORET station 10520001) from 2014 through 2016, , and (3) results of biological sampling conducted in 2010, 2015 and 2016 as part of the DNR/SHL stream biological sampling projects. 

Assessment Explanation

The Class A1 (primary contact recreation) uses are assessed (monitored) as "not supported" based on levels of indicator bacteria that exceeded state water quality criteria. The geometric means of indicator bacteria (E. coli) in the 24 samples collected during the recreational seasons of 2014 through 2016 at DNR station 10520001 near Iowa City were as follows: the 2014 geometric mean was 1288 orgs/100 ml, the 2015 geometric mean was 566 orgs/100 ml, and the 2016 geometric mean was 1028 orgs/100 ml. All three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml. Seventeen of the combined 24 samples (71%) exceeded Iowa’s Class A1 single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and Iowa DNR’s assessment/listing methodology, if the geometric mean is greater than 126 orgs/100 ml., the primary contact recreation uses should be assessed as "impaired" (see pgs 3-33 to 3-35 of U.S. EPA 1997b). Thus, because at least one recreation season geometric mean exceeded criteria for Class A1 uses, these uses are assessed as "not supported."

Results of chemical/physical water quality monitoring at DNR station 10520001 near Iowa City suggest “full support” of the aquatic life uses. Monitoring showed no violations of Class B(WW2) water quality criteria for 35 Ammonia samples (maximum = 1.7 mg/L), 36 Dissolved Oxygen samples (minimum = 5.2 mg/L), 35 pH samples (range = 6.7 to 8.4), 36 Temperature samples (maximum = 27.5°C), 36 Chloride samples (maximum = 92 mg/L), or 36 Sulfate samples (maximum = 95 mg/L) occurred during monitoring from January 2014 to December 2016. According to U.S. EPA guidelines for Section 305(b) water quality assessments (U.S. EPA 1997b, page 3-17), the EPA guidelines allow up to 10% violations of these conventional parameters before impairment of water quality is indicated. Thus, these results thus suggest “full support” of the Class B(WW2) aquatic life uses.

Despite the results of chemical/physical monitoring that suggest “full support” of the Class B(WW2) uses, the results of biological monitoring suggest that these uses should be assessed as “partially supported”. This assessment is based on biological data collected in 2010, 2015 and 2016 as part of the DNR/SHL stream biocriteria project. A series of biological metrics which reflect stream water quality and habitat integrity were calculated from the biocriteria sampling data. The biological metrics are based on the numbers and types of benthic macroinvertebrate taxa and fish species that were collected in the stream sampling reach. The biological metrics were combined to make a fish community index of biotic integrity (FIBI) and a benthic macroinvertebrate index (BMIBI). The indexes rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2016 FIBI score was 34 (fair) and the BMIBI score was 64 (fair).The 2015 FIBI score was 38 (fair) and the BMIBI scores were 48 (fair) and 69 (good).The 2010 FIBI score was 24 (fair) and the BMIBI score was 66 (good). The aquatic life use support was assessed (evaluated) as partially supported (=PS), based on a comparison of the FIBI and BMIBI scores with biological impairment criteria (BIC) established for previous Section 305(b) reports. The biological impairment criteria were determined from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2008. The FIBI BIC for this ecoregion is 36 and the BMIBI BIC for this ecoregion is 51. This segment passed the FIBI BIC 1/3 times and passed the BMIBI BIC 3/4 times in the past seven years.


This aquatic life assessment is now considered "evaluated" based on a change in the 2010 DNR assessment methodology. DNR now requires a segment have two or more biological samples collected from the segment in multiple years over a recent five-year period to be considered “monitored”. This segment had multiple samples collected in the previous seven years (2010-2016); however, the multiple samples were not collected during a five-year period. According to DNR’s assessment/listing methodology, impairments based on “evaluated” assessments are of lesser confidence and are thus not appropriate for Section 303(d) listing (Category 5 of the Integrated Report). DNR does, however, consider these impairments as appropriate for listing under either Category 2b or 3b of the Integrated Report (waters potentially impaired and in need of further investigation). However, despite this change in assessment methodology and type, this waterbody remains in IR Category 5b-t and remains on Iowa’s Section 303(d) list of impaired waters.

Monitoring and Methods
Assessment Key Dates
9/8/2015 Biological Monitoring
10/11/2010 Biological Monitoring
1/9/2014 Fixed Monitoring Start Date
12/5/2016 Fixed Monitoring End Date
10/7/2015 Biological Monitoring
9/19/2016 Biological Monitoring
9/22/2016 Biological Monitoring
Methods
150 Monitoring data more than 5 years old
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
230 Fixed station physical/chemical (conventional plus toxic pollutants)
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
330 Fish surveys
380 Quantitative physical habitat assessment
420 Indicator bacteria monitoring